可见光活性纳米TiO2光催化涂料的抗菌性能研究

基于过渡金属离子掺杂技术,制备了在室内光辐照条件下具有良好光催化抗菌性能的可见光响应型铁掺杂TiO2光催化涂料.研究结果表明,在可见光活性光催化涂料中添加1%的纳米TiO2时,抗菌效果最好,光照24 h后对大肠杆菌、白色念珠球菌、黑曲霉的杀菌率分别达到99.9%、97.2%、82%.采用致孔剂聚乙二醇6 000对光催化...     

无机抗菌剂在建筑涂料中的应用研究

研究了5种无机抗菌剂:锌型沸石抗菌剂、银型沸石抗菌剂、氧化锌晶须复合抗菌剂、纳米TiO2光催化抗菌剂和Ca10-x-yTixZny(PO4)6(OH)2复合抗菌剂在涂料中的应用。以对大肠杆菌(E.coli)的灭菌效果评价抗菌性能。结果表明:锌型抗菌涂料的抗菌效果较差,后4种类型抗菌涂料具有很好抗菌效果。但是,银型抗菌剂和氧化锌晶须复合抗菌剂在涂料中存在易引起涂料变色和难分散问题;纳米TiO2光催化型抗菌剂在涂料中易加快涂料老化;而Ca10-x-yTixZny(PO4)6(OH)2复合抗菌剂既具有良好的抗菌性能,又对涂料的基本性能没有影响,它能够应用到抗菌涂料中。     

无机抗菌剂在建筑涂料中的应用研究

研究了5种无机抗菌剂：锌型沸石抗菌剂、银型沸石抗菌剂、氧化锌晶须复合抗菌剂、纳米TiO2光催化抗菌剂和Ca10-x-yTixZny（PO4）6（OH）2复合抗菌剂在涂料中的应用.以对大肠杆菌（E.coli）的灭菌效果评价抗菌性能.结果表明：锌型抗菌涂料的抗菌效果较差,后4种类型抗菌涂料具有很好抗菌效果.但是,银型抗菌剂和氧化锌晶须复合抗菌剂在涂料中存在易引起涂料变色和难分散问题;纳米TiO2光催化型抗菌剂在涂料中易加快涂料老化;而Ca10-x-yTixZny（PO4）6（OH）2复合抗菌剂既具有良好的抗菌性能,又对涂料的基本性能没有影响,它能够应用到抗菌涂料中.     

纳米生态建筑涂料光催化降解甲醛的研究

以掺加纳米TiO2制备的光催化建筑涂料为催化剂,研究了在紫外光照条件下对气态甲醛的催化降解,并探讨了纳米催化剂晶型、用量和吸附量对光催化降解甲醛的影响。实验结果表明,锐钛型纳米TiO2具有较高的光催化降解甲醛的活性,1h甲醛的降解率可达到70％左右,产物主要为二氧化碳和水;光催化降解甲醛受到涂膜上吸附量的较大影响;该涂料对甲醛的光催化降解反应表现出一级动力学速率规律,且具有良好的线性关系。     

TiO2光催化涂料的制备及其降解甲醛研究

自制TiO2光催化涂料,重点对所制备的涂料在室内进行降解甲醛研究,考察了在不同分散剂、不同光催化剂以及不同甲醛初始浓度、不同光源、不同温度和不同湿度等环境因素下涂料对甲醛降解率的影响。结果表明,选用聚丙烯酸钠离子型分散剂,铜金属掺杂TiO2光催化剂制备的光催化涂料对甲醛降解率达80％以上且具有良好的耐久性,在室温（20℃左右）湿度50％日光灯照射下,甲醛初始浓度5μL时效果最佳。     

掺杂纳米Bi2 WO6的水热合成及其光催化性能研究

采用水热法合成了掺杂纳米Bi2WO6,以罗丹明B为目标降解物,研究了样品在可见光下的光催化性能.采用XRD测试了合成样品的晶体结构,采用BET法测试了合成样品的比表面积,实验结果表明适当浓度的Pb2 、Sr3 和Zr4 离子对纳米Bi2WO6的掺杂均能提高其催化性能,其中掺杂Pb2 、Zr4 更有效,且Pb2 在1%掺杂时效果最好,Zr2 在0.5%掺杂时效果最好.而且,光催化剂在光催化过程中性能稳定,不产生光腐蚀,并具有一定的吸附性能.     

膨胀珍珠岩负载TiO2光催化脱色性能的研究

以钛酸四丁酯为原料 ,膨胀珍珠岩为载体 ,用溶胶 -凝胶法制备可漂浮于水面的负载型TiO2 。利用该负载型TiO2 对罗丹明B(RB)进行光催化脱色实验 ,结果表明 ,浸渍 3次的负载型TiO2 光催化活性最高 ,催化剂最佳用量为 5 0 0mg/10 0mLRB ,经 5h光照 ,对 10 0mL浓度为 1mg/L和 2 .5mg/LRB脱色率分别为 76 .6 7%和 4 7.2 7% ;该催化剂使用寿命长 ,2 5h后催化剂脱色性能没有减弱 ,可重复使用 ;经 8h光照 ,染料废水脱色效果好。     

膨胀珍珠岩负载TiO2光催化脱色性能的研究

以钛酸四丁酯为原料,膨胀珍珠岩为载体,用溶胶-凝胶法制备可漂浮于水面的负载型TiO2.利用该负载型TiO2对罗丹明B(RB)进行光催化脱色实验,结果表明,浸渍3次的负载型TiO2光催化活性最高,催化剂最佳用量为500mg/100mL RB,经5 h光照,对100mL浓度为1 mg/L和2.5 mg/L RB脱色率分别为76.67%和47.27%;该催化剂使用寿命长,25h后催化剂脱色性能没有减弱,可重复使用;经8 h光照,染料废水脱色效果好.     

漂浮型可见光催化剂Fe-N-TiO_2/FP-CTS的制备及其对溶解性柴油的降解

以漂珠为载体,用壳聚糖对漂珠进行改性,并采用溶胶凝胶法,制备了Fe-N共掺杂改性TiO2的漂浮型可见光催化剂(Fe-N-TiO2/FP-CTS),使用X射线衍射(XRD)、紫外可见分光光谱(UV-Vis)、N2吸附-脱附(BET)和扫描电子显微镜(SEM)等分析进行表征。研究结果表明,用壳聚糖改性漂珠可以增加复合光催化剂的比表面积和孔容;相较于N-掺杂TiO2/FP复合光催化剂,Fe-N共掺杂更能促进对复合光催化剂可见光的吸收;光催化4 h后,Fe-N-TiO2/FP-CTS对溶解性柴油的降解率达到61.7%,明显优于Fe-N-TiO2/FP和N-TiO2/FP。当初始pH=5,柴油乳化剂浓度=120 mg/L时,复合光催化剂对溶解性柴油的光催化降解效果最佳。     

纳米二氧化钛复合石墨烯催化剂的制备及处理染料废水

以硫酸钛为原料,采用共沉淀法,制备了一系列纳米二氧化钛复合石墨烯催化剂,采用XRD和FTIR对样品进行表征。通过紫外光照射亚甲基蓝溶液光催化降解实验,研究石墨烯的加入量对TiO2光催化性能的影响,结果表明,TiO2-GO-5具有最佳的光催化性能。在pH=6.00、TiO2-GO-5的投加量为0.070 g/50 mL、光照3 h条件下,100 mg/L亚甲基蓝溶液的脱色率达到最大值为90.52%。     

Bactericidal effect of TiO2 photocatalyst on selected food-borne pathogenic bacteria

Titanium dioxide (TiO(2)) photocatalysts have attracted great attention as a material for photocatalytic sterilization in the food and environmental industry. This research aimed to design a new photobioreactor and its application to sterilize selected food borne pathogenic bacteria, Salmonella choleraesuis subsp., Vibrio parahaemolyticus, and Listeria monocytogenes. The photocatalytic reaction was carried out with various TiO(2) concentrations and Ultraviolet (UV) illumination time. A feasible synergistic effect was found that the bactericidal effect of TiO(2) on all bacterial suspension after UV light irradiation was much higher than that of without TiO(2). As the concentration of TiO(2) increased to 1.0 mg/ml, bactericidal effect increased. However, the bactericidal effect was rapidly abbreviated at TiO(2) concentration higher than 1.25 mg/ml to all selected bacteria. UV illumination time affected drastically the viability of all bacteria with different death rate. Similar trends were obtained from S. choleraesuis subsp. and V. parahaemolyticus that their complete killing was achieved after 3 h of illumination. However, L. monocytogenes was more resistant and its death ratio was about 87% at that time.     

Investigation of the antibacterial effects of silver-modified TiO2 and ZnO plasmonic photocatalysts embedded in polymer thin films

Nanosilver-modified TiO₂ and ZnO photocatalysts were studied against methicillin-resistant Staphylococcus aureus on the surface and against naturally occurring airborne microorganisms. The photocatalysts/polymer nanohybrid films were prepared by spray coating technique on the surface of glass plates and on the inner surface of the reactive light source. The photoreactive surfaces were activated with visible light emitting LED light at λ?=?405 nm. The optical properties of the prepared photocatalyst/polymer nanohybrid films were characterized by diffuse reflectance measurements. The photocatalytic properties were verified with the degradation of ethanol by gas chromatography measurements. The destruction of the bacterial cell wall component was examined with transmission electron microscope. The antibacterial effect of the photocatalyst/polymer nanohybrid films was tested with different methods and with the associated standard ISO 27447:2009. With the photoreactive coatings, an extensive disinfectant film was developed and successfully prepared. The cell wall component of S. aureus was degraded after 1 h of illumination. The antibacterial effect of the nanohybrid films has been proven by measuring the decrease of the number of methicillin-resistant S. aureus on the surface and in the air as the function of illumination time. The photocatalyst/polymer nanohybrid films could inactivate 99.9 % of the investigated bacteria on different thin films after 2 h of illumination with visible light source. The reactive light source with the inner-coated photocatalyst could kill 96 % of naturally occurring airborne microorganisms after 48 h of visible light illumination in indoor air sample. The TEM results and the microbiological measurements were completed with toxicity tests carried out with Vibrio fischeri bioluminescence bacterium.     

溶胶-凝胶法制备复合光催化剂（MWNTs/TiO_2）工艺条件的研究

以多壁碳纳米管（MWNTs）为载体,在煅烧温度200~900℃、煅烧时间1~7 h、溶胶体系pH值为2~10的工艺条件下,采用溶胶-凝胶法制备复合光催化剂（MWNTs/TiO2）。通过其对甲基橙的光催化降解效果对比,评价各种复合光催化剂催化活性之间的差异,结果表明,随着煅烧温度的升高,复合光催化剂中纳米TiO2的晶型由锐钛型逐渐向金红石型转变,500℃时为2种晶型的混合相;pH值为2的强酸性条件有利于形成金红石晶型,pH值为5的中性及弱酸性条件则有利于形成锐钛型,而pH值为3时为2种晶型的混合相;在煅烧温度500℃、煅烧时间3 h、溶胶凝胶体系pH值为3的最佳制备工艺条件下,复合光催化剂催化活性最高,借助扫描电镜发现其TiO2均匀地包覆在多壁碳纳米管管壁上。     

纳米TiO2/活性炭复合光催化剂的制备及其对甲醛气体降解

研究了纳米TiO2/活性炭复合光催化剂对空气中典型污染气体甲醛的光催化降解特性。采用扫描电镜（SEM）表征复合催化剂的表面特征。结果显示,经改性后的纳米TiO2在复合催化剂表面分布均匀,呈球状。对甲醛气体的降解实验显示TiO2负载量为1%时对甲醛的去除效果最好,6 h去除率为61.7%。结果显示复合催化剂把甲醛气体分解成CO2,可以直接排空,无二次污染。     

Mo-N-TiO_2光催化剂的制备、表征及其活性提高机制

以钼酸铵和氨水分别为钼源和氮源,采用溶胶-凝胶法制备了Mo-N-TiO2光催化剂,并对其进行了XRD、XPS和UV-visDRS表征。XRD结果表明,Mo、N共掺杂有效抑制了TiO2晶粒的生长,提高了TiO2由锐钛矿向金红石相的转变温度。UV-vis表明,Mo-N-TiO2光催化剂可见光吸收能力增强,吸收带边明显＂红移＂,且钼酸铵添加量（相对TiO2）为0.5%的样品＂红移＂程度最大,最大吸收带边为550 nm。XPS分析结果表明,Mo取代了TiO2晶格中的部分Ti4＋,以Mo6＋形式存在的,而N以Ti—N及N—Ti—O形式存在。以罗丹明B为模型污染物,重点考察了钼酸铵添加量与焙烧温度对Mo-N-TiO2光催剂性能的影响。结果表明,400℃焙烧下、钼酸铵添加量为0.5%的样品催化活性最好。模拟太阳光下光照120min对罗丹明B的降解率达到96.8%,是纯TiO2的2.42倍。     

Mo-N-TiO2光催化剂的制备、表征及其活性提高机制

以钼酸铵和氨水分别为钼源和氮源,采用溶胶-凝胶法制备了Mo-N-TiO2光催化剂,并对其进行了XRD、XPS和UV-visDRS表征。XRD结果表明,Mo、N共掺杂有效抑制了TiO2晶粒的生长,提高了TiO2由锐钛矿向金红石相的转变温度。UV-vis表明,Mo-N-TiO2光催化剂可见光吸收能力增强,吸收带边明显"红移",且钼酸铵添加量(相对TiO2)为0.5%的样品"红移"程度最大,最大吸收带边为550 nm。XPS分析结果表明,Mo取代了TiO2晶格中的部分Ti4+,以Mo6+形式存在的,而N以Ti—N及N—Ti—O形式存在。以罗丹明B为模型污染物,重点考察了钼酸铵添加量与焙烧温度对Mo-N-TiO2光催剂性能的影响。结果表明,400℃焙烧下、钼酸铵添加量为0.5%的样品催化活性最好。模拟太阳光下光照120min对罗丹明B的降解率达到96.8%,是纯TiO2的2.42倍。     

活性染料K-2BP在环境水体中的光解效应

研究了活性染料K－2BP在TiO2存在下的光催化氧化分解。结果表明,影响光解过程的主要因素是染料浓度、催化剂TiO2的用量和pH。实验条件下,染料样液脱色率可达90％以上,将该法用于实际印染废水的处理,光照6h,脱色率可达70％以上。     

TiO_2膜光催化降解4,4’-二溴联苯的研究

研究了负载于玻璃上的同定化催化剂TiO2膜光催化降解水中4,4'-二溴联苯(4,4'-DBB)的效果,考察了溶液pH值和4,4'-DBB初始浓度等对TiO2膜光催化降解4,4'-DBB的影响,探讨了降解机理.结果表明.TiO2膜光催化降解水中4,4'-DBB的效果良好,紫外光照射8 b,初始浓度为4 mg/L的4,4'-DBB的降解率高达94%,降解速率随着4,4'-DBB初始浓度的增大而下降.在溶液pH=1时,4,4'-DBB的降解效率最高.超声的加入使降解反应的速率加快.经拟合发现4,4'-DBB的降解符合拟一级反应规律,并推导出动力学方程.     

Effect of the carbon coating in Fe-C-TiO(2) photocatalyst on phenol decomposition under UV irradiation via photo-Fenton process

Fe-C-TiO(2) photocatalysts which contained the residue carbon (0.2-3.3 mass%) were prepared from a mixture of TiO(2) and FeC(2)O(4) through the heating at 673-1173 K in Ar. These photocatalysts did not show a high adsorption of phenol, but they were active in photo-Fenton reactions during decomposition of phenol under UV irradiation with addition of H(2)O(2). It was proved that Fe(2+) governed the photoactivity of Fe-C-TiO(2) photocatalysts, it decreased with heat-treatment temperature above 773 K. For comparison, Fe-TiO(2) photocatalyst was prepared by heating TiO(2) and FeC(2)O(4) at 823 K in air for 3h. Phenol decomposition was going much slower on Fe-TiO(2) photocatalyst in comparison with Fe-C-TiO(2), of which mechanism was different, on the former phenol was decomposed by the radical reaction, on the latter through a complex reaction with iron and intermediates of phenol decomposition. Therefore carbon-coating TiO(2) was found to be advantageous for mounting iron and its application for the phenol decomposition via photo-Fenton process.